A Novel Waste Water Treatment Plant for the Disposal of Organic Waste from Mobile Toilets

Total Page:16

File Type:pdf, Size:1020Kb

A Novel Waste Water Treatment Plant for the Disposal of Organic Waste from Mobile Toilets A Novel Waste Water Treatment Plant for The Disposal of Organic Waste from Mobile Toilets A Novel Waste Water Treatment Plant for The Disposal of Organic Waste from Mobile Toilets G. BONIFAZI, R. GASBARRONE, R. PALMIERI, G. CAPOBIANCO, S. SERRANTI Departments of Medical Sciences and Biotechnologies and of Chemical Eng. Materials, Environment- Sapienza University of Rome, Abstract The EU wastewater management industry is continuously looking for innovative technological solutions that can enter the market with a reduced environmental impact. This paper focuses on the problems associated to the disposal of human waste and on the specific market of the so-called mobile toilets. These are independent portable units equipped with sanitary tools that use chemical agents to disinfect the vessel and not connected to the sewer network. With growing awareness towards effective sanitation, mobile toilets have gained immense popularity in recent years and are now widely used at construction sites, event venues, public places, and in several other application like temporary refugee housing, migrants’ camps, military missions, cases of natural disasters, airplanes, trains, campers, caravans and campsites. This paper illustrates a new process for the disposal of organic waste from mobile toilets. Keywords: Waste Water Treatment Plants, Chemical Portable Toilets, Use of sludges in agriculture. 1. Introduction into surface and ground water and to avoid toxic effects on soil, plants, animals and humans. In The use of sludge in agriculture within the EU is most cases, national authorities have currently regulated only by the limits of heavy implemented policies supporting the use of metals (Cd, Cu, Hg, Ni, Pb and Zn) listed in sludge in agriculture, as it is considered to be the Council Directive 86/278/EEC. This document best economic and environmental option to deal is now more than 30 years old and most of the with the increasing quantities of sludge EU countries have introduced more stringent produced. In this context, national authorities requirements and have adopted limits for are seeking to increase confidence in the quality concentrations of other heavy metals, synthetic and safety of products cultivated on sludge organic compounds and microbial fertilised soils. In the context of uncertainties contamination. There is a need to update these concerning the potential impacts on human regulations taking into account the current risks health and the environment of the various associated with the application of sludge to disposal and recycling routes, all main agricultural land. In general, sludge is stakeholders are calling for additional characterized by considerable variability in demonstration activities in order to increase nutrient content depending on the wastewater confidence in the use of sludge in source and treatment process. Although agriculture. The development of agricultural nutrients are essential for plant growth, when recycling depends largely on the possibilities to applied excessively (especially nitrogen and improve the quality of the sludge itself and phosphorus) they may accumulate in soil and increase confidence in sludge quality. This can be leached and transported by drainage implies the prevention of pollution of the waste systems (particularly nitrogen) or can be water at source and improving sludge treatment transported by water erosion (phosphorus bound as well as ensuring the monitoring of sludge to soil particles) and pose a risk to surface water quality. This paper focuses on an innovative and ground water. It is then necessary to have process for the treatment of a particular category the correct safety measures facilitating the of organic residues deriving from the use of prevention of possible leakage of contaminants chemical toilets and from agri-food industry’s production process. 1 International Symposium on Technologies for Smart City – 11th-12th November 2019, Malaga, Spain A Novel Waste Water Treatment Plant for The Disposal of Organic Waste from Mobile Toilets 2. Innovative solutions for the market portable toilets to be provided, the locations and the cleaning and disposal intervals. Cleaning The EU wastewater management industry is with collection of waste is the activity that must continuously looking for innovative ensure the hygiene of mobile toilets in service: it technological solutions that can enter the market consists in emptying the waste collection tank, with a reduced environmental impact. This cleaning it, restoring sanitizing liquids and paper focuses on the problems associated to the consumables, and in the sanitation and disposal of human waste and on the specific disinfection of the toilet. Emptying the market of the so-called mobile toilets (See wastewater collection tank and its relative Figure 1). cleaning are carried out by loading or sucking the resulting waste into tanks mounted on specially equipped vehicles, for subsequent transport to an authorized Wastewater Treatment Plant (WWTP) within the times and in the manner established by the regulations (Figure 2).. Figure 1: Portable chemical toilets. These are independent portable units equipped with sanitary tools that use chemical agents to disinfect the vessel, not connected to the sewer network and intended for the use of a single Figure 2: Traditional disposal of sludge from person and temporarily placed in places where a mobile toilets. number of people have to use them in the absence or insufficiency of fixed sanitation The mobile toilets are in general managed or facilities. With growing awareness towards owned by the same company who carries out the effective sanitation, mobile toilets have gained maintenance cleaning, who makes a specific immense popularity in recent years and are now service available to the applicant (public or widely used at construction sites, event venues, private) dealing with efficiency and hygiene. public places, and in several other application From the maintenance cleaning of a portable like temporary refugee housing, migrants’ toilet, modest quantities of waste result (tens of camps, military missions, cases of natural kilos or litres). The waste deriving from the disasters, airplanes, trains, campers, caravans cleaning of the toilets have the same and campsites. These toilets are also called characteristics as those deriving from the “chemical toilets” because the relative waste cleaning of septic tanks: in all there are collection tanks are usually treated with anti- chemicals, residues of cosmetics, disinfectant fermentation and disintegrating chemical agents detergents, various types of sanitizers in addition with caustic and disinfectant action, which are to waste from human metabolism. This is why, then part of the waste deriving from as such, sludge from chemical toilets cannot be maintenance cleaning and emptying of the tanks normally reused for other purposes and they are themselves. There has been increasing scrutiny commonly sent to WWTP with significant costs over the polluting chemicals currently used in and environmental consequences. The toilets mobile toilets because they are carcinogenic and must be periodically emptied with disposal harmful to the environment and to human health. intervals that depend on the specific application. UNI EN 16194 is the standard specifying the On average, each chemical toilet is completely requirements for services related to the emptied of its content once a week, and every installation of the toilets and those relevant to time a toilet is emptied, about 25 litres of waste chemicals and sanitary products, taking into are collected to be transported to the WWTP. account factors such as hygiene, health and Every time the toilet is emptied it must be safety, cleaning measures, the number of cleaned and sanitized and its tank must be 2 International Symposium on Technologies for Smart City – 11th-12th November 2019, Malaga, Spain A Novel Waste Water Treatment Plant for The Disposal of Organic Waste from Mobile Toilets refilled with clean water along with chemicals. may accumulate in soil and can be leached and On average, the tank is filled with 10 litres of transported by drainage systems or can be water and 1 litre of chemicals. Considering that transported by water erosion and pose a risk to nowadays in Europe there are about 2 million surface water and ground water. It is then chemical toilets in circulation, it can be necessary to have the correct safety measures estimated that every week 2 million litres of facilitating the prevention of possible leakage of chemicals are used to fill the cleaned tanks. contaminants into surface and ground water and When the toiles are emptied, this weekly huge to avoid toxic effects on soil, plants, animals and amount of chemicals will converge in the humans. Since 1986, land application of sewage WWTPs together with the organic materials sludge within the EU has been governed by collected. The environmental problem addressed Council Directive No. 86/278/EEC. It prescribes is characterized by the current need to dispose prior testing of sludge and soil, application of the wastewater in the treatment plant and by the sewage sludge exceeding critical concentrations consequent environmental impact due to the of pollutants to agricultural soil is prohibited, presence of reactive and polluting chemical and soils exceeding permissible concentrations substances. Wastewater in fact, even after cannot receive sewage sludge. This Directive treatment, can end up in areas deemed sensitive has been implemented
Recommended publications
  • Iowa Code Chapter 138 Migrant Labor Camps
    Iowa Code Chapter 138 Migrant Labor Camps 138.1 Definitions. When used in this chapter unless the context otherwise requires: 1. "Camp operator" means the person who has been granted a permit, in accordance with the provisions of this chapter, to operate a migrant labor camp, or portion thereof. 2. "Chemical toilet" means a nonwater carriage toilet facility where human waste is collected in a container charged with a chemical solution for the purpose of disinfecting and deodorizing such waste. 3. "Communicable disease" means any of those diseases regulated by state or local communicable disease laws, ordinances, or regulations. 4. "Department" means the Iowa department of public health. 5. "Director" means the director of public health or the director's designee. 6. "Garbage" means all putrescible animal or vegetable wastes resulting from the handling, preparation, cooking, or consumption of food at a migrant labor camp. 7. "Migrant" means any individual who customarily and repeatedly travels from state to state for the purpose of obtaining seasonal employment in agriculture, including the spouse and children of such individuals, whether or not authorized by law to engage in such employment. 8. "Migrant labor camp" means one or more buildings, structures, shelters, tents, trailers, or vehicles or any other structure or a combination thereof together with the land appertaining thereto, established, operated, or maintained as living quarters for seven or more migrants or two or more shelters. A camp shall include such land or quarters separate from one another if the migrants housed therein work at any time for the same person and the total number of migrants in all such camps is seven or more.
    [Show full text]
  • Use of a Water Treatment Sludge in a Sewage Sludge Dewatering Process
    E3S Web of Conferences 30, 02006 (2018) https://doi.org/10.1051/e3sconf/20183002006 Water, Wastewater and Energy in Smart Cities Use of a water treatment sludge in a sewage sludge dewatering process Justyna Górka1,*, Małgorzata Cimochowicz-Rybicka1 , and Małgorzata Kryłów1 1 University of Technology, Department of Environmental Engineering, 24 Warszawska, Cracow 31- 155, Poland Abstract. The objective of the research study was to determine whether a sewage sludge conditioning had any impact on sludge dewaterability. As a conditioning agent a water treatment sludge was used, which was mixed with a sewage sludge before a digestion process. The capillary suction time (CST) and the specific filtration resistance (SRF) were the measures used to determine the effects of a water sludge addition on a dewatering process. Based on the CST curves the water sludge dose of 0.3 g total volatile solids (TVS) per 1.0 g TVS of a sewage sludge was selected. Once the water treatment sludge dose was accepted, disintegration of the water treatment sludge was performed and its dewaterability was determined. The studies have shown that sludge dewaterability was much better after its conditioning with a water sludge as well as after disintegration and conditioning, if comparing to sludge with no conditioning. Nevertheless, these findings are of preliminary nature and future studies will be needed to investigate this topic. 1 Introduction Dewatering of sludge is a very important stage of the sludge processing. It reduces both sludge mass and volume, which consequently reduces costs of a further sludge processing, facilitates its transport and allows for its thermal processing.
    [Show full text]
  • 2.2 Sewage Sludge Incineration
    2.2 Sewage Sludge Incineration There are approximately 170 sewage sludge incineration (SSI) plants in operation in the United States. Three main types of incinerators are used: multiple hearth, fluidized bed, and electric infrared. Some sludge is co-fired with municipal solid waste in combustors based on refuse combustion technology (see Section 2.1). Refuse co-fired with sludge in combustors based on sludge incinerating technology is limited to multiple hearth incinerators only. Over 80 percent of the identified operating sludge incinerators are of the multiple hearth design. About 15 percent are fluidized bed combustors and 3 percent are electric. The remaining combustors co-fire refuse with sludge. Most sludge incinerators are located in the Eastern United States, though there are a significant number on the West Coast. New York has the largest number of facilities with 33. Pennsylvania and Michigan have the next-largest numbers of facilities with 21 and 19 sites, respectively. Sewage sludge incinerator emissions are currently regulated under 40 CFR Part 60, Subpart O and 40 CFR Part 61, Subparts C and E. Subpart O in Part 60 establishes a New Source Performance Standard for particulate matter. Subparts C and E of Part 61--National Emission Standards for Hazardous Air Pollutants (NESHAP)--establish emission limits for beryllium and mercury, respectively. In 1989, technical standards for the use and disposal of sewage sludge were proposed as 40 CFR Part 503, under authority of Section 405 of the Clean Water Act. Subpart G of this proposed Part 503 proposes to establish national emission limits for arsenic, beryllium, cadmium, chromium, lead, mercury, nickel, and total hydrocarbons from sewage sludge incinerators.
    [Show full text]
  • Energy Recovery from Sewage Sludge: the Case Study of Croatia
    energies Article Energy Recovery from Sewage Sludge: The Case Study of Croatia Dinko Đurđevi´c 1,* , Paolo Blecich 2 and Željko Juri´c 1 1 Energy Institute Hrvoje Požar, 10000 Zagreb, Croatia; [email protected] 2 Faculty of Engineering, University of Rijeka, 51000 Rijeka, Croatia; [email protected] * Correspondence: [email protected] Received: 26 April 2019; Accepted: 16 May 2019; Published: 20 May 2019 Abstract: Croatia produced 21,366 tonnes of dry matter (DM) sewage sludge (SS) in 2016, a quantity expected to surpass 100,000 tonnes DM by 2024. Annual production rates for future wastewater treatment plants (WWTP) in Croatia are estimated at 5.8–7.3 Nm3/people equivalent (PE) for biogas and 20–25 kgDM/PE of sewage sludge. Biogas can be converted into 12–16 kWhel/PE of electricity and 19–24 kWhth/PE of heat, which is sufficient for 30–40% of electrical and 80–100% of thermal autonomy. The WWTP autonomy can be increased using energy recovery from sewage sludge incineration by 60% for electricity and 100% of thermal energy (10–13 kWhel/PE and 30–38 kWhth/PE). However, energy for sewage sludge drying exceeds energy recovery, unless solar drying is performed. 2 The annual solar drying potential is estimated between 450–750 kgDM/m of solar drying surface. The lower heating value of dried sewage sludge is 2–3 kWh/kgDM and this energy can be used for assisting sludge drying or for energy generation and supply to WWTPs. Sewage sludge can be considered a renewable energy source and its incineration generates substantially lower greenhouse gases emissions than energy generation from fossil fuels.
    [Show full text]
  • The Cultural and Environmental Unsoundness of the Chinese Public Squatting-Type Toilet: a Case Study Toward a Sustainable Excreta Treatment System
    Environ. Eng. Res. 2014 March,19(0), 0-0 Research Paper http://dx.doi.org/10.4491/eer.2014.19.0.0 pISSN 1226-1025 eISSN 2005-968X In Press, Uncorrected Proof The Cultural and Environmental Unsoundness of the Chinese Public Squatting-type Toilet: A Case Study toward a Sustainable Excreta Treatment System Jin-Soo Chang Molecular Biogeochemistry Laboratory, Biological & Genetic Resources Institute (BGRI), Hannam University (Jeonming), 505 Inno-Biz Park, 1646 Yuseong-daero, Yeseong-gu, Daejeon 305-811, Republic of Korea Abstract The inconvenient truth of sustainable public squat toilet culture varies among nationalities. According to the adequate environmental management in Yanbian Korean Autonomous Prefecture (YKAP), northern China, this culture may be comfortable to the people of China, yet uncomfortable to the non-Chinese. We conducted a series of field surveys and individual interviews (Chinese n = 1000 and non-Chinese (foreign visitors) n = 100) on several aspects of the public squat toilet: structural properties, waste disposal methods, important factors, and overall satisfaction level. The significant factors in response to the public squat toilets were cleanliness, odor, toilet paper, temperature, soap, other facilities, and presence of cubicles. These factors should be the policy priorities of local government. In addition, 66.2% of Chinese and 91% of foreign visitors desired type E toilets (two full-height partition walls per cubicle, with a door). The results illustrate the nature of a sustainable and aesthetic approach to the culturally and environmentally sound management of various types of public squat toilet in YKAP. The government needs to focus on the future-oriented and excreta treatment management of the sustainable toilet culture for the residents of, and visitors to, YKAP.
    [Show full text]
  • Mobility of Heavy Metals in Municipal Sewage Sludge from Different Throughput Sewage Treatment Plants
    Pol. J. Environ. Stud. Vol. 21, No. 6 (2012), 1603-1611 Original Research Mobility of Heavy Metals in Municipal Sewage Sludge from Different Throughput Sewage Treatment Plants Jarosław Gawdzik1*, Barbara Gawdzik2** 1Faculty of Civil and Environmental Engineering, Kielce University of Technology, Division of Waste Management, Al. 1000-lecia Państwa Polskiego 7, 25-314 Kielce, Poland 2Institute of Chemistry, Faculty of Mathematics and Science, Jan Kochanowski University of Humanities and Sciences, Świętokrzyska 15, 25-406 Kielce, Poland Received: 27 June 2011 Accepted: 11 May 2012 Abstract Sewage sludge heavy metals can be dissolved, precipitated, co-precipitated with metal oxides, and adsorbed or associated on the particles in biological debris. Heavy metals are found in the form of oxides, hydroxides, sulphides, sulphates, phosphates, silicates, organic bindings forming complexes with humic com- pounds, and complex sugars. Polish regulations specifying the maximum levels of heavy metals in municipal sewage sludge used for agricultural purposes refer to the total content of lead, cadmium, mercury, nickel, zinc, copper, and chromium. The aim of our study was to evaluate the mobility of heavy metals in sewage sludge from wastewater treatment plants in Świętokrzyskie Province. Stabilized sewage sludge from wastewater treatment was ana- lyzed in accordance with the extraction method proposed by the Community Bureau of Reference (BCR). Zinc, cadmium, lead, and nickel were determined by means of the standard addition with the use of a Perkin-Elmer 3100-BG FAAS atomic absorption spectrophotometer. Chromium and copper were tested using the FAAS technique. The sequence analysis revealed the presence of heavy metals in all fractions (F-I, F-II, F-III, F-IV).
    [Show full text]
  • Circular Economy in Wastewater Treatment Plant– Challenges and Barriers †
    Proceedings Circular Economy in Wastewater Treatment Plant– Challenges and Barriers † Ewa Neczaj * and Anna Grosser Faculty of Infrastructure and Environment, Czestochowa University of Technology, 42-201 Czestochowa, Poland; [email protected] * Correspondence: [email protected]; Tel.: +48-343-250-917 † Presented at the 3rd EWaS International Conference on “Insights on the Water-Energy-Food Nexus”, Lefkada Island, Greece, 27–30 June 2018. Published: 31 July 2018 Abstract: The urban wastewater treatment plants can be an important part of circular sustainability due to integration of energy production and resource recovery during clean water production. Currently the main drivers for developing wastewater industry are global nutrient needs and water and energy recovery from wastewater. The article presents current trends in wastewater treatment plants development based on Circular Economy assumptions, challenges and barriers which prevent the implementation of the CE and Smart Cities concept with WWTPs as an important player. WWTPs in the near future are to become “ecologically sustainable” technological systems and a very important nexus in SMART cities. Keywords: circular economy; wastewater treatment plant; resource recovery 1. Introduction The circular economy (CE) is the concept in which products, materials (and raw materials) should remain in the economy for as long as possible, and waste should be treated as secondary raw materials that can be recycled to process and re-use [1]. This distinguishes it from a linear economy based on the, ‘take-make-use-dispose’ system, in which waste is usually the last stage of the product life cycle. CE is a concept promotes sustainable management of materials and energy by minimalizing the amount of waste generation and their reuse as a secondary material.
    [Show full text]
  • The Myblok Portable Toilet Was Designed To
    The Myblok portable toilet was designed to meet the needs of small and medium-sized companies. The technology used makes the Myblok portable toilet one of a kind. This portable toilet can be purchased in small quantities. It is available in a wide range of colours and the weight of moulded parts can be chosen according to customer needs. In addition, it is possible to customize the moulding in predefined areas and insert the customer logo. www.tblustar.com TECHNICAL DETAILS Height 230 cm - 90.5 in Width 106 cm - 41.7 in Depth 106 cm - 41.7 in Door Opening 62 cm - 24.5 in Waste Capacity 230 l - 60.8 gal Weight Empty 73 kg - 161 lb Floor Space 94×60 cm - 37×23.6 in Packaging Height 250 cm - 98.4 in COMMERCIAL DATA Minimum order quantity N. 2 Load quantity on a 40HC N. 44 container Quantity full optional in a 40HC N. 32 container Quantity in a truck load N. 48 Quantity full optional in a truck N. 40 load Customize logo on door/door YES frame Customize weight of single YES components Personalization color YES, with extra charge Lead time ex works 20 days + shipping Payment terms Flexible Price Average Transport Not included STANDARD COLORS Classic Blue (600), Light Blue (150), Olive Green (242), Emerald (153), Red (204),Orange (636), Yellow (612), Beige (201), Lime (191), Bright Green (657), Pink (831), White (553), Black (210), Grey (217), Dove Grey (626) ACCESSORIES URINAL, T-CIRCULATE, T-REVOLVE, T-FLUSH, T-WASH, T-LIGHT, T-ROLLER [email protected] www.tblustar.com Rapidloo Demountable Portable Toilet was designed to guarantee more competitiveness to the operators in the industry while complying with the European Directive which states a specific weight-limit allowed by an individual to handle, implemented by Decree 81 dated 2008.
    [Show full text]
  • Aldridge Heated Bidet Toilet Seat Asiento De Inodoro/Bidé Climatizado Sku: 448556, 450177, 450179, 450181
    ALDRIDGE HEATED BIDET TOILET SEAT ASIENTO DE INODORO/BIDÉ CLIMATIZADO SKU: 448556, 450177, 450179, 450181 BEFORE YOU BEGIN TOOLS AND MATERIALS: We recommend consulting a professional if you are HERRAMIENTAS Y MATERIALES: unfamiliar with installing plumbing �xtures. Signature Hardware accepts no liability for any damage to the �oor, walls, framing, plumbing, electrical �xtures, or for personal injury during installation. Adjustable Phillips Wrench Screwdriver Observe all local plumbing and building codes. Llave Destornillador ajustable Phillips Unpack and inspect the seat for shipping damage. If any damage is found, contact our Customer Relations team at 1-800-221-3379. ANTES DE COMENZAR Le recomendamos que consulte a un profesional si no sabe cómo instalar accesorios de plomería. Signature Hardware no asume ninguna responsabilidad con respecto a los daños causados al suelo, paredes, marcos, sistema de plomería, accesorios eléctricos, ni por daños personales que ocurran durante la instalación. Cumpla con todas las normas locales de plomería y construcción. Retire el asiento del empaque y verifique que no se hayan producido daños durante el envío. Si encuentra algún daño, comuníquese con nuestro equipo de Servicios al cliente al 1-800-221-3379. GETTING STARTED Ensure that you have gathered all the required materials that are needed for the installation. CÓMO COMENZAR Asegúrese de haber reunido todos los materiales necesarios para la instalación. REVISED 02/12/2020 For Warranty information, please visit: signaturehardware.com/services/warranty CODES: SHBDS201, SHSK241SHW Para obtener información sobre la garantía, visite: signaturehardware.com/services/warranty SHAM241SWH, SHSR241WH 1 1.800.221.3379 ALDRIDGE HEATED BIDET TOILET SEAT ASIENTO DE INODORO/BIDÉ CLIMATIZADO SKU: 448556, 450177, 450179, 450181 WARNING! ! If using any chemical toilet bowl cleaner, be sure to wipe up any spills that splash onto the plastic IMPORTANT SAFETY INSTRUCTIONS areas of the product.
    [Show full text]
  • Respect Your Forest Products (Tampons and Pads) Into Any Toilet
    into the toilet. Do not put feminine hygiene Respect Your Forest products (tampons and pads) into any toilet. Feminine hygiene products should be wrapped Sequoia National Forest and placed into a trash container. Similarly, do not put disposable baby diapers into any toilet This is information about personal sanitation or portable toilet. Disposable baby diapers may (management of human waste) while visiting the be disposed of in trash containers where Sequoia National Forest. Millions of people visit provided. If trash containers are not provided, the Sequoia National Forest each year and you must pack out the disposable baby diapers visitation is increasing yearly. Improper personal and feminine hygiene products. sanitation and the improper disposal of waste degrade the recreation experience and can Dispersed camping areas are free of charge. degrade water quality and wildlife habitat. Worst Chemical toilet facilities and trash receptacles are of all it can spread diseases. Please help us keep provided in many of these areas for your the Sequoia National Forest clean by following the convenience. We ask that you please use them, sanitation practices below. following the same guidelines explained for developed campgrounds. With in the Sequoia National Forest there are developed campgrounds, dispersed camping, and Where toilet facilities and garbage pick ups wilderness areas. Campfire permits are are not provided Pack-it-out. Whenever it is required when camping in all these areas. feasible, visitors are encouraged to collect human However, camping and the use of campfires wastes and pack them out of the forest. These are not permitted within 25 feet of the Kern wastes need to be disposed of in an approved River's edge, streams and trails.
    [Show full text]
  • Standards for Sanitary Toilets in Coal Mines
    Federal Register / Vol. 68, No. 76 / Monday, April 21, 2003 / Rules and Regulations 19347 that the direct final rule does not have § 56.14131 Seat belts for haulage trucks. ■ 6. Section 57.14131 is amended by a significant economic impact on a * * * * * revising paragraphs (c) and (d) to read as substantial number of small entities. (c) Seat belts required under this follows: section shall meet the requirements of List of Subjects SAE J386, ‘‘Operator Restraint System § 57.14131 Seat belts for surface haulage trucks. 30 CFR Part 56 for Off-Road Work Machines’’ (1985, 1993, or 1997), which are incorporated * * * * * Incorporation by reference, Mine (c) Seat belts required under this safety and health, Surface mining. by reference. (d) The incorporation by reference of section shall meet the requirements of 30 CFR Part 57 these publications is approved by the SAE J386, ‘‘Operator Restraint System Director of the Federal Register in for Off-Road Work Machines’’ (1985, Incorporation by reference, Mine 1993, or 1997), which are incorporated safety and health, Underground mining. accordance with 5 U.S.C. 552(a) and 1 CFR part 51. Copies of these by reference. Dated: April 14, 2003. publications may be examined at any (d) The incorporation by reference of Dave D. Lauriski, Metal and Nonmetal Mine Safety and these publications is approved by the Assistant Secretary of Labor for Mine Safety Health District Office; at MSHA’s Office Director of the Federal Register in and Health. of Standards, Regulations, and accordance with 5 U.S.C. 552(a) and
    [Show full text]
  • Sludge Treatment and Disposal Biological Wastewater Treatment Series
    Sludge Treatment and Disposal Biological Wastewater Treatment Series The Biological Wastewater Treatment series is based on the book Biological Wastewater Treatment in Warm Climate Regions and on a highly acclaimed set of best selling textbooks. This international version is comprised by six textbooks giving a state-of-the-art presentation of the science and technology of biological wastewater treatment. Titles in the Biological Wastewater Treatment series are: Volume 1: Wastewater Characteristics, Treatment and Disposal Volume 2: Basic Principles of Wastewater Treatment Volume 3: Waste Stabilisation Ponds Volume 4: Anaerobic Reactors Volume 5: Activated Sludge and Aerobic Biofilm Reactors Volume 6: Sludge Treatment and Disposal Biological Wastewater Treatment Series VOLUME SIX Sludge Treatment and Disposal Cleverson Vitorio Andreoli, Marcos von Sperling and Fernando Fernandes (Editors) Published by IWA Publishing, Alliance House, 12 Caxton Street, London SW1H 0QS, UK Telephone: +44 (0) 20 7654 5500; Fax: +44 (0) 20 7654 5555; Email: [email protected] Website: www.iwapublishing.com First published 2007 C 2007 IWA Publishing Copy-edited and typeset by Aptara Inc., New Delhi, India Printed by Lightning Source Apart from any fair dealing for the purposes of research or private study, or criticism or review, as permitted under the UK Copyright, Designs and Patents Act (1998), no part of this publication may be reproduced, stored or transmitted in any form or by any means, without the prior permission in writing of the publisher, or, in the case of photographic reproduction, in accordance with the terms of licences issued by the Copyright Licensing Agency in the UK, or in accordance with the terms of licenses issued by the appropriate reproduction rights organization outside the UK.
    [Show full text]